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© Crown copyright INTRODUCTION METHODS High volume in-line water sampling using IDEXX Filta-max xpress® modules and sampling of backwash water for cryptosporidium tesAng RESULTS DISCUSSION CONCLUSIONS ACKNOWLEDGEMENTS REFERENCES Approximate location of pools participating in the study Poolside sampling for bacterial indicators and chemical parameters was undertaken on site at the poolside, including pH, chlorine levels and turbidity Cryptosporidium causes diarrhoeal disease (cryptosporidiosis) with some 6000 confirmed cases in the UK each year. Cryptosporidiosis can be contracted directly through contact with an infected person or animal and a faecal oral route or via consuming contaminated food and/or water. Most outbreaks of Cryptosporidiosis are however associated with recreaConal water exposure, in parCcular swimming pools, including leisure pools. The Cryptosporidium oocysts are resistant to rouCne chemical disinfecCon in swimming pools and present challenges to swimming pool management. Cryptosporidium is not tested for rouCnely in pools; it’s difficult and expensive to test for, not all laboratories are accredited to carry out the tests and there are no quanCtaCve standards, or data are available for the UK. TesCng in outbreaks requires very careful consideraCon, including the interpretaCon of results taken some Cme aKer a potenCal water contaminaCon incident. Primary Aim; Undertake a longitudinal sample survey, over 10 weeks during summer and autumn 2017, to esCmate the background occurrence and concentraCon of Cryptosporidium in six UK leisure pools. Secondary Aims to inform guidance for pool operators to provide data for quanCtaCve microbial risk assessment improve sampling capacity, capability and interpretaCon for public health invesCgaCons Pools Tested 6 volunteer free-form leisure pools with features: slides, wave machines and/or lazy rivers volunteered to support the study and submit samples 4 of the pools were situated in community leisure centres, 2 pools were at large residenAal holiday parks Sampling rigs were installed to allow the filtraCon of high volume water samples from each pool over a 10 week period from early August 2017 Samples were also taken and submiTed for rouCne microbiology. Poolside tests for chemical parameters were also carried out and submiTed as part of the study Public Health Response and Planning Before commencing the study a protocol with the Local Authority and Health ProtecCon Team were agreed for each site. Each pool developed conCngency plans for posiCve samples and adverse events during the project. A pre-sampling review was also carried out on site by each Local Authority prior to the project. www.publichealthwales.org/cryptopoolguidance/ Pool Water Samples Pool water sample volumes through the IDEXX Filta-Max xpress® were 60 to 999 L, median 493 L Samples were taken over 8 to 24 hours IDEXX Filta-Max xpress® filters can block even when turbidity is saAsfactory Oocysts were detected in 12/59 (20%) samples, counts ranged from 0 to 0.116 oocysts / L. 8/12 (66%) detecAons were in August when bather loads were highest Filter Backwash Water Filter backwash water was sampled from 3 pools. Oocysts were detected in 2/29 (7%) samples, from 2 pools; counts were 1 and 4 oocysts / L. DetecAons coincided with oocyst counts in pool waters. TesAng for RouAne Indicators Colony counts of total coliforms, Escherichia coli, and Pseudomonas aeruginosa in 59/60 samples were all zero (1 sample invalid having been sent to the wrong laboratory) Aerobic colony counts @ 37 o C for 24 h in 57 samples were: SaCsfactory (≤10 cfu/ml) 41 (72 %) samples Concerning (10-100 cfu/ml) 4 ( 7 %) samples UnsaCsfactory (>100 cfu/ml) 12 (21 %) sample 3 samples were invalid (1 sent to wrong lab; 2 arrived >24 h aKer sampling) ACC failures and Cryptosporidium detecAons were NOT related This project was carried out with the support and cooperaCon of colleagues within public health, tesCng laboratories, recreaConal water providers and with significant support and input from the Pool Water Treatment Advisory Group. The project was limited in terms of the study Cme, the number of parCcipaCng pools and the configuraCon of the pools, but targeted the pool type and spanned the season most relevant to pool-related incidents . The results serve to inform on acCons that can be considered in response to a public health incident and in response to any posiCve results from any sampling carried out for Cryptosporidium and/or indicator organisms. These data should be supplemented for quanCtaCve microbial risk assessment is required to further develop responses. This requires collaborators and funding to collect bather behaviour data for UK and undertake analysis The risk of detecCon of Cryptosporidium occurred when bather loads were highest. Pool water management is therefore criCcal at these Cmes. Cryptosporidium detecCons and ACC failures were not linked in the p project. Nevertheless, sampling for indicators organisms can conCnue to give surety and verificaCon of general water management. Small numbers of Cryptosporidium oocysts detected in swimming pools can be successfully managed by adhering to PWTAG standards; this also includes ensuring pool water chemistry is monitored and pool plant and equipment is maintained . Access to sampling paraphernalia including liaison with accredited laboratories, and developing an evidence base for environmental cryptosporidia is essenCal to securing effecCve response to incidents Improved sampling capacity, capability and interpretaCon for public health invesCgaCons is required. 1.Anon. The Microbiology of Drinking Water – Part 14- Methods for the isolaCon, idenCficaCon and enumeraCon of Cryptosporidium oocysts and Giardia cysts 2. Anon (2010) The Microbiology of Drinking Water – Part 2 – PracCces and procedures for sampling; Environment Agency 3. The Microbiology of Drinking Water (2012). Part 7 – Methods for the enumeraCon of heterotrophic bacteria. Environment Agency 4. The Microbiology of Drinking Water (2015). Part 8 - Methods for the isolaCon and enumeraCon of Aeromonas and Pseudomonas aeruginosa 5. The Microbiology of Drinking Water (2016). Part 4 - Methods for the isolaCon and enumeraCon of coliform bacteria and Escherichia coli 6. Anon (2017). Swimming Pool Water 3 rd EdiCon Pool Water Treatment Advisory Group, Tamworth The Occurrence of Cryptosporidium in Pools Project, UK, Summer, 2017 Rachel Chalmers, Project Manager, Cryptosporidium Reference Unit , Public Health Wales Rob Johnston, Food Water and Environmental Microbiology Laboratories, Public Health England Megan Luxford, IDEXX, Newmarket Cambs. Rob Miller, LATIS Scientific, Crayford, Kent, UK 2018 High volume sampling rig Laboratory processing (IDEXX) to elute and concentrate oocysts Cryptosporidium oocyst counts by microscopy Poolside sampling for rouAne indicators Laboratory culture (LaAs ScienAfic) TesAng for chemical parameters, poolside Pool Water Treatment Advisory Group, (PWTAG), UK IDEXX , Newmarket, Cambs, UK LaCs ScienCfic , Crayford, Kent, UK CerCkin, Howard Gosling, Total Pool Chemicals Ltd and Jason BasseT TCS BioSciences Ltd: ColorSeed Tintometer Ltd: hand-held and in-line turbidity meters Bourne Leisure, head office Hemel Hempsted Swansea Leisure Centre, Swansea, Wales Merthyr Leisure Centre, Merthyr, Wales Serco Leisure , operators for Mansfield DC Water Meadows Perth Leisure Pool, Perth, Scotland Local authoriCes and Health ProtecCon Teams

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© Crown copyright

INTRODUCTION METHODS

Highvolumein-linewatersamplingusingIDEXXFilta-maxxpress®modulesandsamplingofbackwashwaterforcryptosporidiumtesAng

RESULTS

DISCUSSION CONCLUSIONS ACKNOWLEDGEMENTS

REFERENCES

Approximate location of pools participating in the study

Poolsidesamplingforbacterialindicatorsandchemicalparameterswasundertakenonsiteatthepoolside,includingpH,chlorinelevelsandturbidity

Cryptosporidiumcausesdiarrhoealdisease(cryptosporidiosis)withsome6000confirmedcasesintheUKeachyear.Cryptosporidiosiscanbecontracteddirectlythroughcontactwithaninfectedpersonoranimalandafaecaloralrouteorviaconsumingcontaminatedfoodand/orwater.MostoutbreaksofCryptosporidiosisarehoweverassociatedwithrecreaConalwaterexposure,inparCcularswimmingpools,includingleisurepools.TheCryptosporidiumoocystsareresistanttorouCnechemicaldisinfecConinswimmingpoolsandpresentchallengestoswimmingpoolmanagement.CryptosporidiumisnottestedforrouCnelyinpools;it’sdifficultandexpensivetotestfor,notalllaboratoriesareaccreditedtocarryoutthetestsandtherearenoquanCtaCvestandards,ordataareavailablefortheUK.TesCnginoutbreaksrequiresverycarefulconsideraCon,includingtheinterpretaConofresultstakensomeCmeaKerapotenCalwatercontaminaConincident.PrimaryAim;•  Undertakealongitudinalsamplesurvey,over10weeksduringsummerandautumn2017,toesCmatethe

backgroundoccurrenceandconcentraConofCryptosporidiuminsixUKleisurepools.SecondaryAims•  toinformguidanceforpooloperators•  toprovidedataforquanCtaCvemicrobialriskassessment•  improvesamplingcapacity,capabilityandinterpretaConforpublichealthinvesCgaCons

PoolsTested6volunteerfree-formleisurepoolswithfeatures:slides,wavemachinesand/orlazyriversvolunteeredtosupportthestudyandsubmitsamples4ofthepoolsweresituatedincommunityleisurecentres,2poolswereatlargeresidenAalholidayparksSamplingrigswereinstalledtoallowthefiltraConofhighvolumewatersamplesfromeachpoolovera10weekperiodfromearlyAugust2017SampleswerealsotakenandsubmiTedforrouCnemicrobiology.PoolsidetestsforchemicalparameterswerealsocarriedoutandsubmiTedaspartofthestudyPublicHealthResponseandPlanningBeforecommencingthestudyaprotocolwiththeLocalAuthorityandHealthProtecConTeamwereagreedforeachsite.

EachpooldevelopedconCngencyplansforposiCvesamplesandadverseeventsduringtheproject.Apre-samplingreviewwasalsocarriedoutonsitebyeachLocalAuthoritypriortotheproject.www.publichealthwales.org/cryptopoolguidance/

PoolWaterSamplesPoolwatersamplevolumesthroughtheIDEXXFilta-Maxxpress®were60to999L,median493LSamplesweretakenover8to24hoursIDEXXFilta-Maxxpress®filterscanblockevenwhenturbidityissaAsfactoryOocystsweredetectedin12/59(20%)samples,countsrangedfrom0to0.116oocysts/L.8/12(66%)detecAonswereinAugustwhenbatherloadswerehighestFilterBackwashWaterFilterbackwashwaterwassampledfrom3pools.Oocystsweredetectedin2/29(7%)samples,from2pools;countswere1and4oocysts/L.DetecAonscoincidedwithoocystcountsinpoolwaters.

TesAngforRouAneIndicatorsColonycountsoftotalcoliforms,Escherichiacoli,andPseudomonasaeruginosain59/60sampleswere

allzero(1sampleinvalidhavingbeensenttothewronglaboratory)Aerobiccolonycounts@37oCfor24hin57sampleswere:

SaCsfactory(≤10cfu/ml)41(72%)samplesConcerning(10-100cfu/ml)4(7%)samplesUnsaCsfactory(>100cfu/ml)12(21%)sample

3sampleswereinvalid(1senttowronglab;2arrived>24haKersampling)ACCfailuresandCryptosporidiumdetecAonswereNOTrelated

ThisprojectwascarriedoutwiththesupportandcooperaConofcolleagueswithinpublichealth,tesCnglaboratories,recreaConalwaterprovidersandwithsignificantsupportandinputfromthePoolWaterTreatmentAdvisoryGroup.TheprojectwaslimitedintermsofthestudyCme,thenumberofparCcipaCngpoolsandtheconfiguraConofthepools,buttargetedthepooltypeandspannedtheseasonmostrelevanttopool-relatedincidents.TheresultsservetoinformonacConsthatcanbeconsideredinresponsetoapublichealthincidentandinresponsetoanyposiCveresultsfromanysamplingcarriedoutforCryptosporidiumand/orindicatororganisms.ThesedatashouldbesupplementedforquanCtaCvemicrobialriskassessmentisrequiredtofurtherdevelopresponses.ThisrequirescollaboratorsandfundingtocollectbatherbehaviourdataforUKandundertakeanalysis

TheriskofdetecConofCryptosporidiumoccurredwhenbatherloadswerehighest.PoolwatermanagementisthereforecriCcalattheseCmes.CryptosporidiumdetecConsandACCfailureswerenotlinkedinthepproject.Nevertheless,samplingforindicatorsorganismscanconCnuetogivesuretyandverificaConofgeneralwatermanagement.SmallnumbersofCryptosporidiumoocystsdetectedinswimmingpoolscanbesuccessfullymanagedbyadheringtoPWTAGstandards;thisalsoincludesensuringpoolwaterchemistryismonitoredandpoolplantandequipmentismaintained.Accesstosamplingparaphernaliaincludingliaisonwithaccreditedlaboratories,anddevelopinganevidencebaseforenvironmentalcryptosporidiaisessenCaltosecuringeffecCveresponsetoincidentsImprovedsamplingcapacity,capabilityandinterpretaConforpublichealthinvesCgaConsisrequired.

1.Anon.TheMicrobiologyofDrinkingWater–Part14-MethodsfortheisolaCon,idenCficaConandenumeraConofCryptosporidiumoocystsandGiardiacysts2.Anon(2010)TheMicrobiologyofDrinkingWater–Part2–PracCcesandproceduresforsampling;EnvironmentAgency3.TheMicrobiologyofDrinkingWater(2012).Part7–MethodsfortheenumeraConofheterotrophicbacteria.EnvironmentAgency4.TheMicrobiologyofDrinkingWater(2015).Part8-MethodsfortheisolaConandenumeraConofAeromonasandPseudomonasaeruginosa5.TheMicrobiologyofDrinkingWater(2016).Part4-MethodsfortheisolaConandenumeraConofcoliformbacteriaandEscherichiacoli6.Anon(2017).SwimmingPoolWater3rdEdiConPoolWaterTreatmentAdvisoryGroup,Tamworth

The Occurrence of Cryptosporidium in Pools Project, UK, Summer, 2017

Rachel Chalmers, Project Manager, Cryptosporidium Reference Unit , Public Health Wales     

Rob Johnston, Food Water and Environmental Microbiology Laboratories, Public Health England

Megan Luxford, IDEXX, Newmarket Cambs. Rob Miller, LATIS Scientific, Crayford, Kent, UK

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2018

Highvolumesamplingrig

Laboratoryprocessing(IDEXX)toeluteandconcentrateoocysts

Cryptosporidiumoocystcountsbymicroscopy Poolsidesamplingfor

rouAneindicatorsLaboratoryculture(LaAsScienAfic)

TesAngforchemicalparameters,poolside

PoolWaterTreatmentAdvisoryGroup,(PWTAG),UKIDEXX,Newmarket,Cambs,UKLaCsScienCfic,Crayford,Kent,UKCerCkin,HowardGosling,TotalPoolChemicalsLtdandJasonBasseTTCSBioSciencesLtd:ColorSeedTintometerLtd:hand-heldandin-lineturbiditymetersBourneLeisure,headofficeHemelHempstedSwanseaLeisureCentre,Swansea,WalesMerthyrLeisureCentre,Merthyr,WalesSercoLeisure,operatorsforMansfieldDCWaterMeadowsPerthLeisurePool,Perth,ScotlandLocalauthoriCesandHealthProtecConTeams